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| Registros recuperados : 24 | |
| 8. |  | MARTINEZ, S.; GARBI, M.; ASBORNO, M.; ARTURI, M.; GRIMALDI, M. C. Relacion del rendimiento con parametros bioclimaticos en plantas de tomate defoliadas y sin defoliar. In: CONGRESSO BRASILEIRO DE AGROMETEOROLOGIA, 11.; REUNIAO LATINO-AMERICANA DE AGROMETEOROLOGIA, 2., 1999, Florianopolis, SC. Sessao de paineis... Florianopolis: SBA / EPAGRI / UFSC / UDESC, 1999. nao paginado. CD-ROM.| Biblioteca(s): Embrapa Hortaliças. |
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| 9. | | SARTRE, X. A. de; ALBALADEJO, C.; MARTINS, P.; VEIGA, I.; GRIMALDI, M. Identificação e avaliação da diversidade dos tipos de exploração do ambiente na Amazônia Oriental. Cadernos de Ciência & Tecnologia, Brasília, v.22, n. 1, p.207-220, jan./abr. 2005.| Biblioteca(s): Embrapa Unidades Centrais. |
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| 10. | | BALBINO, L. C.; BRUAND, A.; BROSSARD, M.; GRIMALDI, M.; HAJNOS, M.; GUIMARAES, M. F. Changes in porosity and microaggregation in clayey Ferralsols of the Brazilian Cerrado on clearing for pasture. European Journal of Soil Science, v. 53, n. 2, p. 219-230, June 2002.| Biblioteca(s): Embrapa Arroz e Feijão. |
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| 12. | | BALBINO, L. C.; BRUAND, A.; COUSIN, I.; BROSSARD, M.; QUÉTIN, P.; GRIMALDI, M. Change in the hydraulic properties of a Brazilian clay ferralsol on clearing for pasture. Geoderma, v. 120, n. 3/4, p. 297-307, June 2004.| Biblioteca(s): Embrapa Arroz e Feijão. |
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| 15. | | GRIMALDI, M.; SARRAZIN, M.; CHAUVEL, A.; LUIZAO, F.; NUNES, N.; RODRIGUEZ, M. de R. L.; AMBLARD, P.; TESSIER, D. Effets de la déforestation et des cultures sur la structure des sols argileux d'Amazonie brésilienne. Cahiers Agricultures, v. 2, n. 1, p. 36-47, 1993.| Biblioteca(s): Embrapa Amazônia Ocidental. |
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| 16. | | GRIMALDI, M.; SARRAZIN, M.; CHAUVEL, A.; LUIZAO, F.; NUNES, N.; RODRIGUEZ, M. de R. L.; AMBLARD, P.; TESSIER, D. Effets de la deforestation et des cultures sur la structure des sols argileux d'Amazonie bresilienne. Cahiers Agricultures, v.2, n.1, p.36-47, 1993.| Biblioteca(s): Embrapa Florestas. |
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| 17. | | PIÑA-RODRIGUES, F. C. M.; FREIRE, J. M.; ROLIM, S. G.; JESUS, R. M. de; GRIMALDI, M. C. Maturação e dormência de sementes florestais nativas para a restauração: 20 anos de experiência na reserva natural Vale Linhares, Espirito Santo Ciência & Ambiente, Santa Maria, v. 49, p. 131-152, jul./set., 2014.| Biblioteca(s): Embrapa Agrobiologia. |
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| 18. | | MARICHAL, R.; GRIMALDI, M.; MATHIEU, J.; BROWN, G. G.; SILVA JUNIOR, M. L. da; PRAXEDES, C.; MARTINS, M. B.; VELASQUEZ, E.; LAVELLE, P. Is invasion of deforested Amazonia by the earthworm Pontoscolex corethrurus driven by soil texture and chemical properties? Pedobiologia, v. 55, p. 233-240, 2012.| Biblioteca(s): Embrapa Florestas. |
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| 19. | | MARICHAL, R.; PRAXEDES, C.; BROWN, G. G.; CASTANEDA, E.; DESJARDINS, T.; GOND, V.; GRIMALDI, M.; GUEVARA, E.; JOHAN, O.; SARRAZIN, M.; LAVELLE, P. Earthworm biological traits, soil and landscape characteristics. In: INTERNATIONAL SYMPOSIUM ON EARTHWORM ECOLOGY, 9., 2010, Xalapa. Abstracts. Xalapa: Instituto de Ecologia, 2010. p. 93.| Biblioteca(s): Embrapa Florestas. |
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| 20. | | FEIJOO, A.; MARICHAL, R.; PRAXEDES, C.; RUIZ, D.; CARVAJAL, A. F.; OSWALD, J.; HURTADO, M. Del P.; BROWN, G. G.; GRIMALDI, M.; DESJARDINS, T.; MAX, S.; DECAËNS, T.; LAVELLE, P. Invasion of Pontoscolex corethrurus (Glossoscolecidae, Oligochaeta) in Amazonian landscapes. In: INTERNATIONAL SYMPOSIUM ON EARTHWORM ECOLOGY, 9., 2010, Xalapa. Abstracts. Xalapa: Instituto de Ecologia, 2010. p. 111.| Biblioteca(s): Embrapa Florestas. |
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| Registros recuperados : 24 | |
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 | Acesso ao texto completo restrito à biblioteca da Embrapa Florestas. Para informações adicionais entre em contato com cnpf.biblioteca@embrapa.br. |
Registro Completo
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Biblioteca(s): |
Embrapa Florestas. |
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Data corrente: |
06/08/2015 |
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Data da última atualização: |
06/08/2015 |
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Tipo da produção científica: |
Artigo em Periódico Indexado |
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Circulação/Nível: |
A - 1 |
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Autoria: |
MARICHAL, R.; GRIMALDI, M.; FEIJOO M. A.; OSZWALD, J.; PRAXEDES, C.; RUIZ COBO, D. H.; DEL PILAR HURTADO, M.; DESJARDINS, T.; SILVA JUNIOR, M. L. da; COSTA, L. G. da S.; MIRANDA, I. S.; OLIVEIRA, M. N. D.; BROWN, G. G.; TSÉLOUIKO, S.; MARTINS, M. B.; DECAËNS, T.; VELASQUEZ, E.; LAVELLE, P. |
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Afiliação: |
Raphael Marichal, Université Pierre et Marie Curie; Michel Grimaldi, Centre IRD Ile de France; Alexander Feijoo M., Universidad Tecnológica de Pereira; Johan Oszwald, Université de RenneS; Catarina Praxedes, Museu Paraense Emilio Goeldi; Dario Hernan Ruiz Cobo, Universidad Tecnológica de Pereira; Maria del Pilar Hurtado, CIAT; Thierry Desjardins, Centre IRD Ile de France; Mario Lopes da Silva Junior, UFRA; Luiz Gonzaga da Silva Costa, UFRA; Izildinha Souza Miranda, UFRA; Mariana Nascimento Delgado Oliveira, UFRA; GEORGE GARDNER BROWN, CNPF; Stéphanie Tsélouiko, Université Pierre et Marie Curie; Marlucia Bonifacio Martins, Museu Paraense Emilio Goeldi; Thibaud Decaëns, Université de Rouen; Elena Velasquez, Universidad Nacional de Colombia; Patrick Lavelle, Université Pierre et Marie Curie. |
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Título: |
Soil macroinvertebrate communities and ecosystem services indeforested landscapes of Amazonia. |
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Ano de publicação: |
2014 |
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Fonte/Imprenta: |
Applied Soil Ecology, v. 83, p. 177-185, Nov. 2014. |
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DOI: |
http://dx.doi.org/10.1016/j.apsoil.2014.05.006 |
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Idioma: |
Inglês |
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Notas: |
XVI International Colloquium on Soil Zoology & XIII International Colloquium on Apterygota, 2012, Coimbra. Selected papers. |
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Conteúdo: |
Land use changes in the Amazon region strongly impact soil macroinvertebrate communities, whichare recognized as major drivers of soil functions (Lavelle et al., 2006). To explore these relations, wetested the hypotheses that (i) soil macrofauna communities respond to landscape changes and (ii) soilmacrofauna and ecosystem services are linked. We conducted a survey of macrofauna communities andindicators of ecosystem services at 270 sites in southern Colombia (department of Caqueta) and north-ern Brazil (state of Pará), two areas of the Amazon where family agriculture dominates. Sites representeda variety of land use types: forests, fallows, annual or perennial crops, and pastures. At each site weassessed soil macroinvertebrate density (18 taxonomic units) and the following ecosystem service indi-cators: soil and aboveground biomass carbon stock; water infiltration rate; aeration, drainage and waterstorage capacities based on pore-size distribution; soil chemical fertility; and soil aggregation. Signifi-cant covariation was observed between macrofauna communities and landscape metric data (co-inertiaanalysis: RV = 0.30, p < 0.01, Monte Carlo test) and between macrofauna communities and ecosystemservice indicators (co-inertia analysis: RV = 0.35, p < 0.01, Monte Carlo test). Points located in pastureswithin 100 m of forest had greater macrofauna density and diversity than those located in pastures withno forest within 100 m (Wilcoxon rank sum test, p < 0.01). Total macroinvertebrate density was signifi-cantly correlated with macroporosity (r2= 0.42, p < 0.01), as was the density of specific taxonomic groups:Chilopoda (r2= 0.43, p < 0.01), Isoptera (r2= 0.30, p < 0.01), Diplopoda (r2= 0.31, p < 0.01), and Formicidae(r2= 0.13, p < 0.01). Total macroinvertebrate density was also significantly correlated with available soilwater (r2= 0.38, p < 0.01) as well as other soil-service indicators (but with r2< 0.10). Results demonstratethat landscape dynamics and composition affect soil macrofauna communities, and that soil macro-fauna density is significantly correlated with soil services in deforested Amazonia, indicating that soilmacrofauna have an engineering and/or indicator function. MenosLand use changes in the Amazon region strongly impact soil macroinvertebrate communities, whichare recognized as major drivers of soil functions (Lavelle et al., 2006). To explore these relations, wetested the hypotheses that (i) soil macrofauna communities respond to landscape changes and (ii) soilmacrofauna and ecosystem services are linked. We conducted a survey of macrofauna communities andindicators of ecosystem services at 270 sites in southern Colombia (department of Caqueta) and north-ern Brazil (state of Pará), two areas of the Amazon where family agriculture dominates. Sites representeda variety of land use types: forests, fallows, annual or perennial crops, and pastures. At each site weassessed soil macroinvertebrate density (18 taxonomic units) and the following ecosystem service indi-cators: soil and aboveground biomass carbon stock; water infiltration rate; aeration, drainage and waterstorage capacities based on pore-size distribution; soil chemical fertility; and soil aggregation. Signifi-cant covariation was observed between macrofauna communities and landscape metric data (co-inertiaanalysis: RV = 0.30, p < 0.01, Monte Carlo test) and between macrofauna communities and ecosystemservice indicators (co-inertia analysis: RV = 0.35, p < 0.01, Monte Carlo test). Points located in pastureswithin 100 m of forest had greater macrofauna density and diversity than those located in pastures withno forest within 100 m (Wilcoxon rank sum test, p < 0.01). Total macroinver... Mostrar Tudo |
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Palavras-Chave: |
Landscape; Macro-invertebrates; Macroinvertebrado; Paisagem deflorestada; Soil services. |
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Thesagro: |
Ecossistema. |
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Thesaurus NAL: |
Amazonia. |
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Categoria do assunto: |
-- |
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Marc: |
LEADER 03588naa a2200433 a 4500
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008 2014 bl uuuu u00u1 u #d
024 7 $ahttp://dx.doi.org/10.1016/j.apsoil.2014.05.006$2DOI
100 1 $aMARICHAL, R.
245 $aSoil macroinvertebrate communities and ecosystem services indeforested landscapes of Amazonia.$h[electronic resource]
260 $c2014
500 $aXVI International Colloquium on Soil Zoology & XIII International Colloquium on Apterygota, 2012, Coimbra. Selected papers.
520 $aLand use changes in the Amazon region strongly impact soil macroinvertebrate communities, whichare recognized as major drivers of soil functions (Lavelle et al., 2006). To explore these relations, wetested the hypotheses that (i) soil macrofauna communities respond to landscape changes and (ii) soilmacrofauna and ecosystem services are linked. We conducted a survey of macrofauna communities andindicators of ecosystem services at 270 sites in southern Colombia (department of Caqueta) and north-ern Brazil (state of Pará), two areas of the Amazon where family agriculture dominates. Sites representeda variety of land use types: forests, fallows, annual or perennial crops, and pastures. At each site weassessed soil macroinvertebrate density (18 taxonomic units) and the following ecosystem service indi-cators: soil and aboveground biomass carbon stock; water infiltration rate; aeration, drainage and waterstorage capacities based on pore-size distribution; soil chemical fertility; and soil aggregation. Signifi-cant covariation was observed between macrofauna communities and landscape metric data (co-inertiaanalysis: RV = 0.30, p < 0.01, Monte Carlo test) and between macrofauna communities and ecosystemservice indicators (co-inertia analysis: RV = 0.35, p < 0.01, Monte Carlo test). Points located in pastureswithin 100 m of forest had greater macrofauna density and diversity than those located in pastures withno forest within 100 m (Wilcoxon rank sum test, p < 0.01). Total macroinvertebrate density was signifi-cantly correlated with macroporosity (r2= 0.42, p < 0.01), as was the density of specific taxonomic groups:Chilopoda (r2= 0.43, p < 0.01), Isoptera (r2= 0.30, p < 0.01), Diplopoda (r2= 0.31, p < 0.01), and Formicidae(r2= 0.13, p < 0.01). Total macroinvertebrate density was also significantly correlated with available soilwater (r2= 0.38, p < 0.01) as well as other soil-service indicators (but with r2< 0.10). Results demonstratethat landscape dynamics and composition affect soil macrofauna communities, and that soil macro-fauna density is significantly correlated with soil services in deforested Amazonia, indicating that soilmacrofauna have an engineering and/or indicator function.
650 $aAmazonia
650 $aEcossistema
653 $aLandscape
653 $aMacro-invertebrates
653 $aMacroinvertebrado
653 $aPaisagem deflorestada
653 $aSoil services
700 1 $aGRIMALDI, M.
700 1 $aFEIJOO M. A.
700 1 $aOSZWALD, J.
700 1 $aPRAXEDES, C.
700 1 $aRUIZ COBO, D. H.
700 1 $aDEL PILAR HURTADO, M.
700 1 $aDESJARDINS, T.
700 1 $aSILVA JUNIOR, M. L. da
700 1 $aCOSTA, L. G. da S.
700 1 $aMIRANDA, I. S.
700 1 $aOLIVEIRA, M. N. D.
700 1 $aBROWN, G. G.
700 1 $aTSÉLOUIKO, S.
700 1 $aMARTINS, M. B.
700 1 $aDECAËNS, T.
700 1 $aVELASQUEZ, E.
700 1 $aLAVELLE, P.
773 $tApplied Soil Ecology$gv. 83, p. 177-185, Nov. 2014.
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